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CHAPTER 2
41
"Future of Earth -- Now or never"
-- Sandra Postel
METALLURGICAL MATERIALS
'I STEEL PLANT SLAG
f FOUNDRY SLAG tziNC SMELTER SLAG :MILL SCALES ZFERROMANGANESE ~LLOY
THEIR GENESIS,AVAILABILITIES, REDUCTION BEHAVIOURS
2.1 STEEL PLANT SLAG GENESIS AND AVAILABILITY
Slag is the name applied to the fused product
formed by the action of the flux upon the gangue of an
ore or fuel, or upon the oxidised impurities of the
metal. The slag results from the nuetralization of
materials of acidic and basic nature, hence corresponds
roughly to salts formed in aqueous solution during
chemical reactions at ordinary temperature (1). On
account of their fusibility, chemical activity,
dissolving power and low density, slags furnish the
means by which impurities are separated from the
metal, and removed from the furnace in iron and steel
making processes.
In the blast furnace, solid charge materials
(iron ore, coke and limestone), are charged in the
vertical shaft of the furnace at the top and hot air
blast is blown through tuyeres (Fig 2-1) located at the
bottom. The oxygen from the preheated blast combines
with the carbon of coke, and generates heat and carbon
monoxide. The gas phase containing mainly N2
and CO
ascends upwards through the charge which reacts with
and extracts heat from the gas phase. Eventual] y; the
charge melts, and metal and slag thus produced are
stratified and separated to obtain the metal.
The main chemical reactions are the reduction
of iron oxide and the burning of coke (2).
42
2C + 02 ---7 2CO
2Fe0 + 3CO ---7 3C02 + 4Fe
Fe 2o 3 + 3C ---7 3CO + 2Fe
C0 2 + c -t 2CO
Limestone and Dolomite which are used
charge get calcined as
Caco3 -7 CaO
MgC03~ MgO
+
+
as flux in the
The resulting basic oxides combine with the gangue
oxides to form the slag (Fig 2-1).
Composition of blast furnace slag is rather
complex. Up to thirty different chemical elements occur
in the slags mainly in the form of oxides. The
principal ones include
MgO. Usually present in lesser amounts are :FeO, MnO,
so3 , P2o 5 , Tio2 , v2o 5 and others. Depending on the
value of the so called modulus of basicity,
[ %Ca0 + %Mg0 ) all the blast furnace slags obtained %Si02 + %Al 2o3
at ferrous metallurgy enterprises can be divided· into
three groups, namely acidic, basic and neutral (3).
The chemical compositions of hl ast furnace
slags in Russia have been reported (31 in the fnlln~inJ•
43
Gas -+---
200• Stock line Expulsion of water
600
Sponge Iron formation
1200.
•
Molten metal &. Slag Formation
1500" Combustion
Bell LCone
T hroal --5m---
3 Fe 2o3•CO ~ 2 Fe30~• C02
Fe 3 O~+CO;;!: 3 Fe O•C02
Stack
Cylinder or BellY
-- --- 6.5 m ----
Bosh
FeO+C ::;:!:" Fe+CO
MnO•·C:;:!: Mn+CO
Si0t2C ~ Si+2CO
p2
o5+5C =2P+5CO
MnS+CaO+C
= Mn +CaS+CO
CaO+SI 02 = CaS;OJ
C02 + C = 2 CO
Tuyerts __,..
I Hearth Slag notch ~
~---7.5m----
C +02-:.C02
FIG.-
~ Mrtal Tap Hole
DIAGRAM OF A BLAST FURNACE SHOWING THE
CHEMICAL REACTIONS.
44
45
ranges (%) :
Si02
35.0-39.9; A12o
3 7.0-16.3; CaO 30.4-46.3;
MgO 2.3-14.3; FeO 0.2-0.7; MnO 0.3-2.9;
s 0.5-4.7.
The composition of slags depends upon chemical
composition of raw materials, operation factors and
grades of metals to be produced. The chemical
composition of blast furnace slags, in Indian steel
industries, has been reported to be in the following
ranges Si02 33-42"/.; Al 2o3 10-15"/o; CaO 36-45%; t1g0
3-12%; S 1-3%; FeO 0.3-2%; MnO 0.2-1.5% (4). The
average chemical composition of blast furnace slag of
Bhilai Steel Plant to which the work described is
rel ated1 has been reported as follows Sio2
34-53%;
Al 20 3 22. 38'7o; CaO 34-7 5%; MgO 5. 80%; FeO 0. 81'7o; Mn
0.59%; s 0.74% (4,5).
Indian slags are characterised by comparatively
a high alumina content resulting from the use of more
aluminous iron ore and high ash metallurgical coke (6).
As high alumina content is known to increase viscosity
of melt, dol amite is added to get low viscosity slags
for proper operation of blast furnace. Mn-ore is added
to minimise harmful effects of sulphur and allowing it
to increase Strength and toughness of steel.
Steel melting shops in steel manufacturing
industries form another source for the disch;H[!C of
slags. The production of slags from this source is
about 20 kg/tonne of steel manufactured, compared to
500-600 kg per tonne of hot metal in the case of blast
furnace. The composition of SMS slag has been reported
as follows Si02 10-20%, FeO 8-10%; CaO 30-40%; NgO
3-10%; Al 2o3 4-10% <7).
The total amount of the blast furnace slags
currently turned out by Russian industrial enterprises
exceeds 50-52 million tonnes a year, and comprise the
largest single waste of the metallurgical melting
process (3). About 80% blast furnace slag and 28.5% SMS
slag stand utilized in Russia,Granulated slags (54% of
the total production) and broken slags ( 35/o) are
produced on the largest seal e. In India, the usage of
blast furnace slag is based on the mode of production
of the slag, namely air-cooled variety has application
for use as aggregate for portland cement concrete, for
road construction, as rail road ballast, as roofing
material, as sewage filter media in ceramic-ware
making, as soil conditioner, in slag wool manufacture
and as land-fill material in low lying areas and
embankments. The granulated variety of the slag is used
in· the manufacture of slag based portland cement, slag
bricks, mortars, opaque and transparent glass and as a
land-fill material for worked-out mines, road1vays and
railway embankments. The installed capacity of the
ingot steel envisaged in India by 2000 A.O. is 7'i
46
47
million tonnes. The world steel production figures of
1990 and 1991 were 735.3 and 769.8 million tonnes
respectively (8). Steel productions in India during the
same years were 15.0 and 17.1 million tonnes respectively
(8). The average rate of discharge of slags in India is
615 kg/tonne of steel manufactured (9). The figures
speak of the massive availability of steel plant s1 ags
in India.
2.2 FOUNDRY SLAGS : GENESIS AND AVAILABILITY
A foundry is that in which metals are reduced to
fluid state and poured into moulds of various types.
When the liquid metal has cooled, and the mound has been
removed, the finished pro~uct is called a casting. Nowa
days, cas tin:; represents an extreme] j important sector
in components used in engineerin6. By mel tin;;, it is
possible to obtain highly complicated shapes for
components which would otherwise be extremely expensive,
or even impossible to produce by machine tools (10).
~1eta1 founding on modern 1 ines for mass production
of industrial castings was started in India in the later
half of 19th century. Today, this section forms the
backbone of the engineering industry, manufcturing a
wide range of various range of castings of various
specifications such as plain carbon, stainless
steel , wear resistant, corrosion resistant
and creep resistant steels. The weight of these
castings may range from few grams to hundred tonnes
single piece, and simple to most intricate ones to meet
the ever increasing technological requirements of the
country and overseas market. Indian railways account
for around 40% of the total demand for steel castings
in the country (11).
48
Steel foundries in India are located at Durg,
Raipur, Agra, Delhi, Ghaziabad, Faridabad, Varanasi,
Kanpur, Luckhnow, Calcutta, Asansol, Burnpur, Dhanbad,
Bokaro, Jamshedpur, Rourkela, Durgapur, Bombay, Nagpur,
Ahmedabad, Baroda, Jhansi, Visakhapatnam, Salem, Madras
and Indore. Today, over three dozen foundries
manufacture about ninty thousand tonnes of alloy steel
castings per year ( 12). In the region of Durg and
Raipur districts of Hadhya Pradesh, five major steel
foundries manufacture over 5000 tonnes of alloy steel
and precision castings over a year. In foundry process,
scrap iron, iron ore, ferromanganese, lime stone,
dolomite, bauxite and coke are fed into an electric arc
furnace in specified ratios to produce molten iron of
desired specifications. The molten metal is then poured
in especially prepared silica moulds to produce
castings of various sizes and uses. The castings are
then taken otit and dipped in water for quenching. About
2% of the total molten iron produced is clischaq~ed in
the form of slag, and scraped out of the f11rnacc
periodical] v.
The sl.ags of the foundries located in
Durg-Raipur region have been reported to have the
following composition (%)
3.1-5.6; Al 2o3 17.5-19.5; Mno 4 4.3-4.5; CaD 13.4-16.5;
MgO 5.8-6.4; Na 2o 0.5-0.8; K2o 0.2-0.3 (13). The slag
has further been reported to be alkaline in nature. The
pH of the 10% slurry in water has been reported to be
in the range of 9.8-10.2. Its solubility at 20°C has
been reported to be between 4.2-4.5 mg (13).
2.3 ZINC SMELTER SLAGS THEIR GENESIS
Sinter and coke are fed into the sh~ft of the
smelter furnace from the top, and the blast air enters
through tuyeres in the lower part of the furnace. Lead
and slag are tapped from the furnace hearth, and
furnace gas and zinc vapour leave the shaft through the
furnace off-take. The overflowing slag from the hearth
is directed into a launder in which it is granulated by
high pressure water jets. The slag is shifted through
perforated buckets from the slag pit to the slag bin at
a rate of 50 tonnes/hour. The slag from the bin is then
discharged into dumpers which transport it to the area
earmarked for the slag storage. The slag could be
described as silicates of Ca,Al ,Fe, Zn etc which form
gl~ss like granules during the granulation process. It
is vitreous and nonporous with a bulk densitv of 2.00
49
tonne/m5 . The main partie] e size ( 78%) is +500 micron.
The typical chemical composition of the slag is as
follows (14) Fe2o3 32.2-40.0, Si02 18.0-22.0, CaO
12.0-16.0, AJ2o
3 7.0-9.0, Zn 4.0-10.0, MgO 2.0-3.5, S
1.0-2.5, Pb 1.0-2.0, Cu 0.1-0.2, As 0.2-0.3.
2.4 MILL SCALES THEIR GENESIS
In the process of rolling, semi-finished
products like ingots, blooms, slabs, billets etc have
to be reheated before these are rolled into finished
products. This reheating process is necessiated by the
logistics or scheduling of the rolling operations
and/or the need to condition the surfaces of the semi
finished work pieces.
50
Basically, the reheating operation is intended
to raise as uniformly as possible the temperature of
the blooms, slabs or billets etc to the l.evels
appropriate for hot rolling. This operation is carried
out in a reheating furnace. In most reheating furnace
of conventional design, work pieces undergo scaling due
to the oxidation. Although this results in a yield loss
of 1-5%, it is often regarded as desirable in removing
superficial defects from the surfaces of the work
pieces. Optimum temperature for rol 1 ing depends upon
the composition of steel being used. For high carhons
it is J065-1100°C. For medium carhons the range is
1090-1145°C, an1l for low carbons it is about 1250°C.
The phenomenon of oxidation of steel surfaces
is known as scaling, and the oxides produced in hot
rolling process are known as mill seal e. The mechanism
of scale formation is regarded as of a dynamic nature,
with the highest oxides Fe 2o3 (haematite) being formed
first and then successively reduced by available iron
to Fe3o
4 (magnetite) and then to FeO.
Oxidation of the surface may also result into
decarbonisation of the surface layers because carbon
can easily migrate to the surface to form carbon
monoxide and carbon dioxide.
2.5 FERROMANGANESE ALLOY ITS FORMATION AND COHPOSITION
Ferromanganese is used in steel making as an
alloying material, and for deoxidising purposes. Based
on carbon content, ferromanganese has been divided into
two types ( 1 I High carbon ferromanganese, and ( 2)
Medium carbon ferromanganese. The percent composition
of high carbon ferromanganese is C 7 .5, Mn 70-74, Si
1.50, P 0.43, S 0.05, Fe-Balance. The medium carbon
ferromanganese has the following percent composition :
C 2.0, ~!n 70-75, Si 2.0, P 0.2, S 0.01, Fe-Balance.
Ferromanganese is a costly material.
The ferromanganese a 11 oy is proclucccl 1 n
electric arc ftlrnace. The raw materials
1111111111111mlllll T 12080
1 fJ..c9c
51
manganese ore, pig iron scrap, lime stone and dolomite.
These materials are melted, and the alloy and the slag
are tapped either separately or together in ladles. The
ferromanganese lumps are crushed and screened to
desired size,
2.6 METALLURGICAL MATERIALS AS ELECTROCHEMICAL REDUCTANTS : EXPLORATORY STUDIES
The types of the metallurgical materials having
been indentified , they were subjected to qualitative
tests to detect their capabilities to cause
electrochemical reduction. the tests were carried out
as follows :
(i) Reaction with silver nitrate solution
\-Jeighed quantities ( 10 g each) of the powdered
samples of the metallurgical materials (blast furnace
slag, foundry slag, zinc smelter slag, mill scales and
ferromanganese alloy) were placed in separate glass
vessels, and SO ml of silver nitrate solution (0.1 M)
was added to each, after which the mixtures were kept
for observation. A shiny deposition of metallic silver
was observed in each reaction mixture confirming that
the silver ions IE 0 = •0.799VI had undergone
electrochemical reduction in each case resulting in the
precipiration of silver metal (A!!-+ + e-+ Ag 0 ) .
52
( ii) Study of the re1 ative rates of the reduction reacactions of the metallurgical materials
For this purpose, weighed quantities (5 g each)
of the samples of the above stated metallurgical
materials were added to 250 ml of a silver nitrate
53
solution (O.OSM) in separate glass vessels. Aliquots (Sml ·
each) were drawn at known intervals and the
concentrations of Ag +
' FeZ+ and Mn 2+ ions were
determined in each aliquot. The silver ion
concentration was determined ti trimetrically using
standard solution (Siol as indicator (15). The ferrous
ion concentration was determined spectrophotometrically
using 1, 10 orthopenanthroline solution, measuring
absorbance at 515 nm (15), after the removal of
interference of Ag+ by precipitation as AgCl (15). The
manganese concentration was also determined
spectrophotometrical] y using KI04
as oxidant, and
measuring the absorbance at 545 nm after boiling in
HN03 solution (15).
The result obtained have been shown in Table
2-1. The relationships between variations in
concentrations of Ag(I), Fe(II) and Mn(Il) ions with
duration for each of the selected metallurgical
materials have been shown in Fig 2-2.
S.N
o.
1.
2 .
3.
4.
5 .
~1aterial s
~leta]
Th
eir
in
itia
l T
heir
co
ncen
trati
on
(m
g/1
) fo
un
d
aft
er
use
d
Ion
s co
ncen
trati
on
s (m
g/1
) 30
m
in
~
Ste
el
Pla
nt
Ag
(I)
53
.88
3
0.7
1
Gra
nu
late
d
Fe
(II)
N
IL
32
.00
sl
ag
M
n (I
I)
NIL
4
.10
Fo
un
dry
A
g C
I l
53
.88
3
2.6
7
Sla
g
Fe
(II)
N
IL
29
.00
M
n (I
I)
NIL
4
.00
Zin
c S
melt
er
Ag
(I)
53
.88
1
5.9
6
Sla
g
Fe
(II)
N
IL
51
.10
M
n (I
I)
NIL
1
.10
Mil
l S
cale
A
g(I
) 5
3.8
8
12
.21
F
e (I I)
NIL
9
7.0
0
Mn (I
I)
NIL
N
IL
Fer
rom
ang
anes
e A
g(I
) 5
3.8
8
11
.32
F
e( I
I)
NIL
4
2.0
0
Mn (I
I)
Nil
6
2.8
0
*M
ult
ipli
cati
on
fa
cto
r 1
03
for
all
A
g(I
) co
ncen
trati
on
s
60
min
90
m
in
28
.09
2
0.3
4
34
.00
4
0.0
0
4.2
0
4.
70
28
.52
2
8.0
3
29
.50
3
3.1
0
4.0
0
4.2
1
15
.28
1
2.9
0
55
.60
7
.40
1
.24
1
. 51
10
.01
6
.10
1
05
.00
1
12
.00
N
IL
NIL
10
.24
4
.30
4
3. o
o·
52
.00
6
4.6
0
70
.00
12
0
min
16
.52
4
3.0
0
4.7
0
22
.83
3
4.0
0
4.
30
12
.80
6
2.1
0
1. 5
3
2.5
0
11
5.0
0
NIL
Nil
6
1.0
0
79
.00
150
min
16
.52
4
3.0
0
4.
70
22
.42
2
5.0
0
4.5
0
12
.80
6
3.0
0
1.
60
NIL
1
15
.00
N
IL
NIL
6
1.0
0
79
.00
C1'l ~
1()
c,olsrF:EL
' so '
I, 0·
30-
0
PL;\NT GFU\NUL/\lF:O SL/\G
--~ r·,,
0 Fe
·J JO GO 90 120 150
LJUn,.~TICf,) ( rninUtQS)
Fe
MILL SCALE
Mn
Fe
FERROMANG.<\NESE ALLOY
Ag
0 30 GO 90 120 150
DURATION ( mtnutes)
-2 7::c: '1,\Y:::c: 01 ELI'ClP'•rtrrc; !C/\L PF/ICTIOIJS IN I'RESEUCE OF DIFFi:RENT
·:.--.- ~:.L :.~,r\:rr?·,' !_:O.
55
56
2. 7. METALLURGICAL MATERIALS DETERMINATION OF
REDUCTION CAPACITIES
INTRODUCTION
The metallurgical material chosen for their
applications in the present work are Steel Plant (blast
furnace) slag (granulated), steel foundry slag, zinc
smelter slag, mill scales and ferromanganese alloy.
Before undertaking the study of their applications it
was considered helpful to eva 1 uate the relative
capacities of these metallurgical wastes for causing the
el ctrochemical reduction. The electrochemical reduction
capacity of a metallurgical material has been
arbitrarily taken here as the weight of silver ions in
milligrams precipitated by 1 g of the waste in particle
forms of 100 mesh size when allowed to remain in contact
with 10 ml of a O.lM AgN0 3 solution for a duration of
60 seconds at the room temperature. There may be some
imperfections in this arbitrary definition on account of
the probabi 1 ity of the rem ova 1 of silver ions by
processes other than electrochemical reduction such as
surface adsorption, ion-exchange, chemical precipitation
etc. However, the capacity as defined here has been
found to be of practical use and served the purpose of
the intended investigations to a reasonable extent.
MATERIALS AND METHODS
~~~rle Collection Samples ( 1 kg Cilchl of the
granul a red slag of a steel plant, and foundrv sl ar ~o.·crc•
57
collected from Bhilai Steel Plant and Himmat Steel Works
located at Bhilai and Kumhari (Distt.Durg) respectively.
The sample of zinc smelter slag 1 kg) was received
from the zinc smelter plant located at Chittorgarh
(Rajasthan). The samples of mill scale and
ferromanganese alloy 1 kg each) were obtained from
Bhil ai Steel Plant. The samples were powdered by a
grinding mill, and fractions of the powdered samples of
100 mesh size were obtained. In the case of
ferromanganese alloy, the samples were prepared by
drilling of the blocks followed by powdering in the
mill. Two more samples, one of iron filings and another
of aluminium foils were obtained from the local market,
and simi 1 a rl y processed. These samples corresponded to
two reactive metals in their elemental states, and have
been chosen here so that the reduction capacities of the
selected metallurgical wastes could be compared with
those of these reactive metals.
PROCEDURE
Reagent Solutions
Silver Nitrate Solution (0.1 M) : Prepared by dissol'ving
1.69R8 g AgN0 3 (BDH AnalaR make) in 100 ml distilled
water.
S0dium Chloride Solution (0.1 Ml p r er ilr cd hv
di!>solv!ng O.'i84'i g NaCl (1\Dil An<JlaR) in 100 ,.,]
distilled w<Jter.
58
Potassium Chromate Solution : Prepared by dissolving 5 g
Potassium Chromate (BDH AnalaR) in 100 ml distilled
water.
Accurately weighed quantities (1 g each) of the
powdered samples were taken in 100 ml beakers and mixed
with 10 ml of the silver nitrate solution. At the close
of 60 seconds the mixtures were decanted through
sintered crucible, and the silver ion concentrations
determined titrimetrically using NaCl and potassium
chromate solution as indicator (16). The decrease in the
concentration of silver ions was then found out by
calculation. The procedure was repeated in case of all
the seven samples used here. The electrochemical
reduction capacities of the samples thus found out have
been shown in Table 2-2 below.
Table 2-2 THE ELECTROCHEMICAL REDUCTION CAPACITIES OF
METALLURGICAL SAMPLES
Samples used
Iron filings
Aluminium foils
Electrochemical reduction capacities ( mg Ag/g of samples)
Blast furnace granulated slag
Foundry slag
23.6
14.9
4.1
4.0 11.6 Zinc Smelter slag
Hill scale
Ferromanganese alloy 20.2
2 2. 1
59
RESULTS AND DISCUSSION
In has been found that the most available and
economical waste material is the granulated slag
obtained from the blast furnaces of the steel plants.
This is followed by the foundry slags.The other
materials are in the following order of their
availabilities Zinc smelter slag > mill scale >
ferromanganese alloy. The last material, i.e., the
ferromanganese alloy is the most expensive, and its
inclusion here is to examine the response of a material
containing mostly iron and manganese.
The response of the selected materials towards
electrochemical reduction has been found positive when
each of the material exhibited a shiny deposition of
metallic silver on interaction with silver nitrate
solution. When the relative rates of reduction reactions
of the metallurgical materials were examined under
similar conditions, it was found that the ferromanganese
alloy and the mill seale exhibited the fastest rates
fall owed by zinc smelter slag, steel plant slag and the
foundry slag.
The products of electrochemical reactions· are
most] y Fe( II) and ~In( II) ions in the case of steel plant
slag, foundry slag, zinc smelter slag and ferromanganese
alloy. The mill scale did not exhibit any release of
manganese ions due to the absence of this el C'r.cnt i 11 it.
60
The zinc smelter slag is susceptible to release Zn(II)
and Pb(III ions also in view of the significant presence
of these in the slag. (The formation of Zn II, and Pb II
ions was not studied, hence their values not shown in
the data table). By taking the total quantities of the
reaction products into account, the reaction rates of
the materials were found to be in the following order :
ferromanganese > mill scale > zinc smelter slag > steel
plant slag > foundry slag. This sequence is almost the
same as found and reported above. When the reduction
capacities of the metallurgical materials were examined,
the same were found in the following order
ferromanganese alloy > mill scale > zinc smelter slag >
steel plant slag > foundry slag. The reduction
capacities of iron filings and aluminium foils as pure
metallic materials were also examined. While the
reduction capacity of iron filings was found close to
that of ferromanganese, that of aluminium foil was found
to be 1 ow.
Taking into view the overall aspects of economy,
availability, reaction rates and the reduction
capacities, the granulated slag of the steel plant was
found t9'be the most suitable material, although it was
found superior to only the foundry slag and Jess
effective than the ferromanganese al 1 oy, mil 1 seale and
the zinc smelter slag. Therefore, for making the methncls
cost effective
applications, the
preferred.
and
use
expanding
of steel
the scope
plant slag
of
has
their
he en
61
SUMMARY
This chapter is devoted mostly to the
exploratory work. The metallurgical materials such as
steel plant slag, foundry slag, zinc smelter slag, mill
scale and ferromanganese alloy were indentified here as
the source materials for causing the electrochemical
reduct ion of toxic species, the details of which are
being given in subsequent chapters. The details with
regard to the genesis, availabilities, compositions and
the reduction behaviours of the materials have been
collected through the literature survey, and also
investigated experimentally where necessary. The steel
plant slag was found to be the most available and
economical waste material for the proposed studies. This
is followed by foundr~slag, zinc smelter slag, mill
scales and ferromanganese alloy. The last named material
was found to
mostly for
principles.
demonstrate
indications
reactions.
be expensive, and its
the
All
verification of
these materials
qualitative as well
inclusion here was
the underlying
were found to
as quantitative
of causing electrochemical reduction
The relative rates of reductions of these
materials lvere studied, and the same were found in the
follmving order ferromanganese alloy > mi 11 seale >
zinc smelter slag>steel plant slag > foundry slag. The
reduction caracities, in terms of weight of silver ions
reduced per gram of material used, were experimentally
determined, and the same were found to be in the
following order ferromanganese alloy > mill scale >
zinc smelter slag> steel plant slag> foundry slag.
Taking into account the overall aspects of
economy, ·availability, reaction rates and the reduction
capacities, "' the g~,nulated slag of steel plant was found
to be the most suitable material, although it was found
superior to only the foundry slag and less effective
than the ferromanganese alloy, mill scale and the zinc
smelter slag.
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REFERENCES
1. US Steel Publn., "Making, Shaping and Treating of Steel" United States Steel, (7th edn.) ( 1957) 174-75.
2. Tupkary, R.H.,"Introduction to Modern Iron Making" Khanna Publishers, Delhi (1982) 128-129.
3. Gromov,B.V.,"Utilization of Metallurgical Slags in the Soviet Union", Industry and Environment, 7 (2) (1984) 12-13.
4. Singh,Narinder, Shrivastava,K.N.,Krishnan,R.M., Nijhavan,B.R.,"Scope for Utilization of Slags and Related \~astes from Indian Iron and Steel Plants", Symposium on Utilization of Metallurgical Wastes, Jamshedpur (March 10-18,1964) 192-195.
5. BSP Publn.,"Horks Visit Notes -- An Orientation Guide'', Training and Management Department, Bhilai Steel Plant, Bhilai (1986) 54.
6. Chopra,S.K. ,Taneja,C.A. ,"Utilization of the Indian Blast Furnace Slags", Symposium on Utilization of Metallurgical \~astes, Jamshedpur, (March 10-18, 1964) 224,225.
7. Bhinde ,A.D. ,Sundarsan,B.B., "Solid-Waste Management in Developing Countries",INSDOC, New Delhi (1983) 30.
8. Anonymous,"\~orld Steel in figures-1992", Iron and Steel Engineer, 69, 10 (1992),47-48.
9. Sangameshwaran,K.R.,"Coke Furnaces", Transactions of ~!etals, 31 ( 2) ( 1978) 121.
Economy in Blast the Indian Institute of
10. "The new Caxton Encyclopedia",Vol.VI,Thames Publishing Corporation, London, ( 1969).
11. "The New Book of Knowledge", Vol.II, Gralier Incorporated, New York, (1973).
12. CEI Pub ln., "Handbook of Statistics", Confederation of Engineering Industries, New Delhi (1987).
13. Hoitra,J.K. and Pandey,G.S. ,"Steel Foundry Wastes: Study of Pollutants of Slags and Effluents", ~dian Journal of Environ.Protecs 9 (5) (1CJR9).
14. ~!ukherjce,A.D.! Pre.mkumar,G. and Dhana Sckaran,R., Pnmary Lead Smel tlng at HZL, Hind Zinc Tech 3 No.I, (19<J1). --' '
15. Bassett ,J., Denny ,C. H. and Mendham ,J., Vogel's Quantitative Inorganic Analysis (4th Language Book Society/Longman,Essex, (1986).
Textbook of edn), English
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